Iranpour R, Cox H H J, Oh S, Fan S, Kearney R J, Abkian V, Haug R T
City of Los Angeles Bureau of Sanitation, CA, USA.
Water Environ Res. 2006 Feb;78(2):170-80. doi: 10.2175/106143005x89625.
The highest quality of biosolids is called exceptional quality. To qualify for this classification, biosolids must comply with three criteria: (1) metal concentrations, (2) vector-attraction reduction, and (3) the Class A pathogen-density requirements. The City of Los Angeles Bureau of Sanitation Hyperion Treatment Plant (HTP) (Playa del Rey, California) meets the first two requirements. Thus, the objective of this study was to ensure that HTP's biosolids production would meet the Class A pathogen-reduction requirements following the time-temperature regimen for batch processing (U.S. EPA, 1993; Subsection 32, Alternative 1). Because regulations require the pathogen limits to be met at the last point of plant control, biosolids sampling was not limited to immediately after the digesters, i.e., the digester outflows. The sampling extended to several locations in HTP's postdigestion train, in particular, the last points of plant control, i.e., the truck loading facility and the farm for land application. A two-stage, thermophilic-continuous-batch process, consisting of a battery of six egg-shaped digesters, was established in late 2001 for phase I of this study and modified in early 2002 for phase II. As the biosolids were discharged from the second-stage digesters, the Salmonella sp. (pathogen) and fecal-coliform (indicator) densities were well below the limits for Class A biosolids, even though the second-stage-digester temperatures were a few degrees below the temperature required by Alternative 1. Salmonella sp. densities remained below the Class A limit at all postdigestion sampling locations. Fecal-coliform densities were also below the Class A limit at postdigestion-sampling locations, except the truck-loading facility (phases I and II) and the farm for final use of the biosolids (phase II). Although federal regulations require one of the limits for either fecal coliforms or Salmonella sp. to be met, local regulations in Kern County, California, where the biosolids are land-applied, require compliance with both bacterial limits. Additional work identified dewatering, cooling of biosolids after the dewatering centrifuges, and contamination as possible factors in the rise in density of fecal coliforms. These results provided the basis for the full conversion of HTP to the Los Angeles continuous-batch, thermophilic-anaerobic-digestion process. During later phases of testing, this process was demonstrated to produce fully disinfected biosolids at the farm for land application.
最高质量的生物固体被称为特级质量。要获得这一分类,生物固体必须符合三项标准:(1)金属浓度,(2)减少病媒吸引,以及(3)A类病原体密度要求。洛杉矶市环境卫生局海波龙处理厂(HTP)(加利福尼亚州普拉亚德尔雷)满足前两项要求。因此,本研究的目的是确保HTP的生物固体生产在遵循间歇处理的时间-温度方案后(美国环境保护局,1993年;第32节,替代方案1)符合A类病原体减少要求。由于法规要求在工厂控制的最后一点达到病原体限制,生物固体采样不限于紧接消化器之后,即消化器流出物处。采样扩展到HTP消化后流程中的几个位置,特别是工厂控制的最后一点,即卡车装载设施和用于土地施用的农场。2001年末建立了一个由六个卵形消化器组成的两级嗜热连续间歇工艺用于本研究的第一阶段,并于2002年初进行了修改用于第二阶段。当生物固体从第二阶段消化器排出时,沙门氏菌属(病原体)和粪大肠菌群(指示菌)密度远低于A类生物固体的限值,尽管第二阶段消化器的温度比替代方案1要求的温度低几度。在所有消化后采样位置,沙门氏菌属密度均低于A类限值。除了卡车装载设施(第一阶段和第二阶段)以及用于生物固体最终使用的农场(第二阶段)外,消化后采样位置的粪大肠菌群密度也低于A类限值。尽管联邦法规要求满足粪大肠菌群或沙门氏菌属其中之一的限值,但生物固体进行土地施用的加利福尼亚州克恩县的地方法规要求同时符合两种细菌的限值。进一步的工作确定脱水、脱水离心机之后生物固体的冷却以及污染是粪大肠菌群密度升高的可能因素。这些结果为HTP全面转换为洛杉矶连续间歇嗜热厌氧消化工艺提供了依据。在后续测试阶段,该工艺被证明能在用于土地施用的农场生产完全消毒的生物固体。